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Urban Watershed Challenge Storm Sewers & Watershed Models
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Delineation Questions Height-of-land delineation is altered by storm sewer Gravity and force main Gravity and force main Do we need to correct for storm sewers? Significance of storm sewers is scale dependent Significance of storm sewers is scale dependent Can we correct for storm sewers?
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Semi-Automated Delineation Burn streams into DEM Run initial delineation on modified DEM Check with local sources and experts Review DOQs Modify streams and repeat the process
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Boundary Disagreement Stream modified DEM boundary Manually delineated boundary
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Storm Sewer Data Acquire data Mostly CAD format Mostly CAD format Import to GIS Georeference no metadata no metadata unknown coordinate systems unknown coordinate systems
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Challenge #1: Georeferencing Spatial adjustment tool used to fix georeferencing problem
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Georeferenced Data
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Example: Effect of Lift Stations Stream modified DEM boundary Manually delineated boundary
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Challenge #2: Jurisdictional Issues Stream modified DEM boundary Manually delineated boundary City of Edina Storm Sewer Hennepin County Storm Sewer
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Example: Revised Delineation
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Challenge #3: Directionality Limited use of directionality
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Challenge #4: Connectivity Interrupted by other feature types maintenace access holes maintenace access holes Interrupted by missing surface water feature open ditch open ditch
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Challenge #5: Attributes Inconsistent attributes between sources Typically limited attributes Attributes may be as graphical annotation
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Summary of Challenges Unknown coordinate systems Overlapping jurisdictions Lack of directionality Lack of connectivity Inconsistent and sparse attributes
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Urban Watershed Models Three basic algorithms for water quality modeling of urban watersheds Event-mean concentration (EMC) Event-mean concentration (EMC) Regression model (rating curve) Regression model (rating curve) Build-up / wash-off Build-up / wash-off
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EMC Simplest approach - event mean concentration (EMC) Many published values Often monitoring is land use specific EMCs area-weighted based on land use
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EMC Land Use TNTPTSSBOD Low-density residential 1.770.1819.14.4 Single family residential 2.290.3277.4 Multi-family residential 2.420.4971.711 Low-intensity commercial 1.180.15818.2 High-intensity commercial 2.830.4394.37.2 Industrial1.790.3193.99.6 Highway2.080.3450.35.6 Pasture2.480.47694.35.1 General agricultural 2.320.34455.33.8 Open space 1.250.05311.11.45 Adapted from Harper, H. H. (1998). Land Use Specific EMCs (mg/L)
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EMC Advantages Allows evaluation of various land use scenarios Allows evaluation of various land use scenarios It’s simple (cheap) It’s simple (cheap) Disadvantages Too simple? Too simple? Ignores high variability (spatially and temporally) Ignores high variability (spatially and temporally) No statistically significant difference between urban land uses (NURP) No statistically significant difference between urban land uses (NURP) Examples – Pondnet (Walker)
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Regression Models Another approach is to develop empirical relationships between runoff concentration and predictor variables Flow Flow Land use Land use Soils Soils Climate Climate
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Regression Models 1 10 100 1000 1101001000 Flow (cfs) TSS (mg/L)
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Regression Models Advantages Allows evaluation of various land use & soils Allows evaluation of various land use & soils Still pretty simple Still pretty simple Disadvantages Can account for spatial and temporal variability Can account for spatial and temporal variability Not mechanistic Not mechanistic Examples - Tasker & Driver (1988), SWMM, SWAT
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Build-Up / Wash-Off Build-up & wash-off Mass balance of pollutants on impervious surfaces A constant rate of accumulation A first-order rate of non-runoff removal Accumulation Non-runoff removal
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Build-Up / Wash-Off 0 5 10 15 20 25 01020304050 Antecedent Dry Days Mass (kg/m2) 0 0.2 0.4 0.6 0.8 1 00.511.522.5 Daily Rainfall Intensity (in/hr) Fraction Mass Remaining Build-Up Wash-Off
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Build-Up / Wash-Off Build-Up / Wash-Off Advantages More mechanistic approach More mechanistic approach Hopefully more broadly applicable Hopefully more broadly applicable Disadvantages More complicated More complicated Lack the data needed to calibrate this model Lack the data needed to calibrate this model Doesn’t address contributions from pervious areas Doesn’t address contributions from pervious areas Examples – P8, SLAMM, SWMM, SWAT
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